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Successional Categorization of European Hemi-Boreal Forest Tree Species

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Successional Categorization of European Hemi-Boreal Forest Tree Species plants Review Successional Categorization of European Hemi-boreal Forest Tree Species Raimundas Petrokas 1 , Virgilijus Baliuckas 1 and Michael Manton 2,* 1 Department of Forest Genetics and Tree Breeding, Institute of Forestry, Lithuanian Research Centre for Agriculture and Forestry, Kaunas distr LT-53101, Lithuania; [email protected] (R.P.); [email protected] (V.B.) 2 Institute of Forest Biology and Silviculture, Vytautas Magnus University, Studentu 11, Akademija, Kaunas LT-53361, Lithuania * Correspondence: [email protected] Received: 7 September 2020; Accepted: 14 October 2020; Published: 16 October 2020 Abstract: Developing forest harvesting regimes that mimic natural forest dynamics requires knowledge on typical species behaviors and how they respond to environmental conditions. Species regeneration and survival after disturbance depends on a species’ life history traits. Therefore, forest succession determines the extent to which forest communities are able to cope with environmental change. The aim of this review was to (i) review the life history dynamics of hemi-boreal tree species in the context of ecological succession, and (ii) categorize each of these tree species into one of four successional development groups (gap colonizers, gap competitors, forest colonizers, or forest competitors). To do this we embraced the super-organism approach to plant communities using their life history dynamics and traits. Our review touches on the importance and vulnerability of these four types of successional groups, their absence and presence in the community, and how they can be used as a core component to evaluate if the development of the community is progressing towards the restoration of the climatic climax. Applying a theoretical framework to generate ideas, we suggest that forests should be managed to maintain environmental conditions that support the natural variety and sequence of tree species’ life histories by promoting genetic invariance and to help secure ecosystem resilience for the future. This could be achieved by employing harvesting methods that emulate natural disturbances and regeneration programs that contribute to maintenance of the four successional groups. Keywords: climatic climax; life history; forest disturbance; gap colonizers; gap competitors; forest colonizers; forest competitors; forest dynamics; forest management 1. Background Forests are complex systems of interacting organisms; to manage them for tree species composition and production we need thorough knowledge of the variety of tree species’ life histories and how they interact. Within the hemi-boreal forest climatic zone there are three main forest disturbance regimes that host a variety of successional characteristics: (i) stand succession (large or stand replacing disturbance such as severe fire, windthrows, or current clear felling), (ii) cohort dynamics (related to partial disturbances of a stand such as a low intensity ground fire or forest thinning), and (iii) gap dynamics (such as small patch or a fallen tree) [1]. Succession is a sequential shift of patterns and processes in terms of the relative abundance of dominant species [2]. The succession of forest stands and patches largely determines the extent to which forest communities are able to cope with changes in environmental conditions and forest loss due to natural disturbances or human activity [3–6]. Forest disturbances trigger successional events that lead to climatically determined end communities or climatic climax, generally regarded as a position of stability in the development of vegetation [7–9]. Plants 2020, 9, 1381; doi:10.3390/plants9101381 www.mdpi.com/journal/plants Plants 2020, 9, 1381 2 of 11 The first definition of climax was described by Clements [10] as the ability of species composition to remains stable for more than one tree generation (i.e., the tree species replace themselves) in the absence of disturbance other than tree deaths due to old age. Thus, a forest that can regenerate naturally with the same composition over time can qualify as natural climax. Although Clements’ [10] dynamic ecology concept is still valid [11], it does not represent the boundless factors impacting ecological succession. For example, the role and importance of both biotic and abiotic factors in predicting species distributions remains unclear [12–16]. Therefore, no clear conclusion can be drawn as to the successional position of tree species [10]. The probability of species survival and succession after disturbance depends on a species’ genetic profile to deal with a variety of environmental characteristics [17]. In other words, a tree’s life history traits define its position along its successional pathway that includes functional strategies for reproduction or resource capture [18]. The fundamental principle underlying the theory of invariance is that the laws of nature always have the same form for all observers [19]. This implies that all the elements of any developing living system interact, and thus all elements are ecologically equivalent, as the essence of ecological law and processes lies in invariance by which a living system following a disturbance returns to its stable state [20,21]. From a wildlife perspective, each organism, population, and community have different environmental scales in both time and space [22], and individual species may impact another species’ life history traits [23,24]. Thus, there are different perceptions about the interactions among species (that otherwise can survive virtually the same for millions of years), which proceed towards the ecological equivalence of climatically determined end communities [25]. Primary forests exist in a delicate but stable climax with all other components of the ecosystem; not one component can change without compensating changes in the others. For example, harvesting or thinning a forest stand will inevitably be followed by changes in the soil profile, vegetation, and life occurrence [9]. Generally, the dynamics of forest communities can be controlled by a set of ecologically invariant life-history traits of tree species turnovers [9,26–29]. The natural tendency of forest succession is towards climatic climax, whereas the succession of forests after human activity (e.g., fire, grazing, and soil deterioration due to over-cultivation) can result in adaptation of biotic climaxes [9]. Therefore, forest restoration that aids the recovery of forest structure, ecological functioning, and biodiversity towards those typical of a climax forest by the re-instatement of ecological processes is needed [30]. From an organism-centered perspective, developing forest management and exploitation regimes that mimic the natural conditions as closely as possible requires the determination of the degree to which typical species behaviors are responsible for the emergence of climatic climax [31–36]. The aim of this review was two-fold: (i) to review the life history dynamics of hemi-boreal tree species found in Lithuania in the context of ecological succession, and (ii) to categorize Lithuania’s forest tree species into four successional development classes. Finally, we discuss how they can be used to evaluate if the development of the community is progressing towards the restoration of the climatic climax. 2. Successional Categorization of Forest Tree Species in Lithuania Lithuania (62,000 km2) is situated in the hemi-boreal climatic zone (i.e., the transitional zone from temperate to boreal forests) and is affected by the humid marine climate of the Baltic Sea [37]. The natural potential forest cover of Lithuania is predominantly composed of five main forest types: (i) hemi-boreal spruce forest with mixed broadleaved trees (55%), (ii) mixed oak–hornbeam forests (22%), (iii) boreal and hemi-boreal pine forests with partial broadleaved trees (18%), (iv) lime-pedunculate oak forests (4%), and (v) species-poor oak and mixed oak forests (1%) [38]. Thus, the natural climatic climax of the region for tree species consisted of Scots pine (Pinus sylvestris L.), Norway spruce (Picea abies L.) Karst), birch (Betula pendula Roth and B. pubescens Ehrh), alder (Alnus glutinosa L. Gaertn. and A. incana L. Moench), English oak (Quercus robur L.), small-leaved lime (Tilia cordata Mill.), and European hornbeam (Carpinus betulus L.) [39]. Currently approximately 33% of Lithuania is forested with Scots pine, Norway spruce, and birch forming the dominating forest stand types [40]. The full range of hemi-boreal forest species found in Lithuania and their life history dynamics can be found in Table1. Plants 2020, 9, 1381 3 of 11 Table 1. A simplified framework for the life history dynamics for hemi-boreal tree species in Lithuania. See Supplementary Materials 1 for more details on each species. Life History Traits Tree Species Dominant Stand Soil Moisture A Soil Fertility B Life Expectancy [42] Shade Tolerance Hardiness C [43] Successional Strategy Proportion [40] [41,42] [41,42] (Harvesting Age) [44] Dominant Forest Tree Species Scots pine (Pinus sylvestris L.) 34.6% 1–3 and 5 1–3 and 5 Intolerant 9 300–400 (110) Disturbance generalist Norway spruce (Picea abies L. Karst) 20.9% 3–4 3–4 Intermediate 7 200–300 (71) Succession generalist Silver birch (Betula pendula Roth) 22.0% 2–5 2–4 Intolerant 9–10 150 (61) Disturbance generalist Black alder (Alnus glutinosa L. Gaertn) 7.6% 4–5 3–4 Intermediate 7 180–200 (61) Disturbance generalist Grey alder (Alnus incana L. Moench) 5.9% 2–5 3–4 Intermediate 9 50–70 (31) Disturbance generalist
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